An experimental study on recolonization and succession of marine macrobenthos in defaunated sediment

Hypoxia/anoxia in coastal waters is a world wide problem which often results in mass mortality and defaunation of benthos. In this study, field experiments were carried out to examine recolonization and succession of macrobenthic infauna in defaunated sediments, and the time required for recovery from complete defaunation to a stable community. Trays (33 cm length × 25.5 cm width × 11 cm depth) of defaunated sediment were exposed at the subtidal of a pristine site in subtropical Hong Kong. Temporal changes of macrobenthic communities in defaunated sediment were analyzed by univariate and multivariate statistics, and compared with those in undisturbed natural sediment at the same site. Initial colonization of macrobenthos occurred rapidly. A total of 42 species was found, with an average of 258 animals per tray and 24 species per tray recorded in the first month. Abundance showed a small peak (496 animals per tray) after 3 months, reached a sharp peak (1154 animals per tray) after 6 months, and declined thereafter. Species number increased gradually, reached a maximum (68 species per tray) after 9 months, and then decreased. Recolonization was predominantly contributed by larval settlement rather than adult migration. Temporal changes in abundance, species number and diversity of the macrobenthic community in defaunated sediment resemble the spatial changes along a decreasing pollution gradient previously defined by other authors. Results of this experiment suggest that newly available sediment may allow more species to colonize (or coexist) than sediment pre-occupied by an established community. This is probably due to less interspecific competition in the former habitat. No significant difference in abundance or species richness was observed between defaunated and natural sediments after 15 months, suggesting that a stable community had been achieved, although minor variations in species composition were still discernible between defaunated and natural sediments. Received: 24 May 1999 / Accepted: 20 October 1999     

聚苯乙烯基硫代磺酸钾树脂的合成及其与卤代烃的反应

由聚苯乙烯基磺酰氯树脂与硫化氢钾反应制备聚苯乙烯基硫代磺酸钾树脂（Ｉ）,树脂Ｉ与亲电的卤代烃反应,生成聚苯乙烯基硫代磺酸酯树脂（Ⅱ）,树脂Ⅱ经过乙硫醇处理,使卤代烃结构部分以不对称二硫醚的形式游离下来,用ＧＣ／ＭＳ对其结构进行鉴定。从不对称二硫醚的结构可推导出原卤代烃的结构,所制备的聚苯乙烯基硫代磺酸钾树脂的转化效率为１．１１ｍｍｏｌ·ｇ＾－１。     

羊角月芽藻摄取磷形态的动力学研究

将湖水中的磷分成总溶解磷,溶解反应磷,总反应磷、溶解的水解性磷,溶解的光解性磷。研究其在羊角月芽过程中的变化。     

某铀矿山辐射环境历史演化

调查了某铀矿山居民区环境空气中氡及其子体浓度、空气吸收剂量率和水中放射性核素含量。在已有资料的基础上,对历史时期的辐射环境进行分析。结合实地监测数据,对辐射剂量估算,评价该矿山辐射环境的现状。结果表明,该矿山排放的放射性物质确实对当地的居民产生了一定影响,在所调查的时间段内,该矿山评价区域由放射性物质排放所致关键子区居民的最大年有效剂量为0.52mSv;无论是历史时期还是现状,其关键核素都是^222Rn。指出,为了进一步降低放射性物质对环境的影响,首先应考虑减少^222Rn的排放。     

制药废水硝化-反硝化除氮研究

含高浓度氮的制药废水经好氧生化处理后,虽然出水的ＣＯＤ,ＢＯＤ５均可达到行业排放标准,但ＴＮ仍高达约１７０ｍｇ／Ｌ。本研究在曝气池中设置填料,利用生物膜外层好氧,内层缺氧厌氧的条件,使硝化－反硝化脱氮在同一构筑物内进行,ＮＨ３－Ｎ和ＴＮ去除率分别可达约９０％和７０％。在本试验条件范围内,温度越高,负荷越低,硝化和反硝化作用越完全,ＮＨ３－Ｎ和ＴＮ去除率越高。     

Biofilm structure and its influence on clogging in drip irrigation emitters distributing reclaimed wastewater

Using reclaimed wastewater for crop irrigation is a practical alternative to discharge wastewater treatment plant effluents into surface waters.However,biofouling has been identified as a major contributor to emitter clogging in drip irrigation systems distributing reclaimed wastewater.Little is known about the biofilm structure and its influence on clogging in the drip emitter flow path.This study was first to investigate the microbial characteristics of mature biofilms present in the emitters and the effect of flow path structures on the biofilm microbial communities.The analysis of biofilm matrix structure using a scanning electron microscopy (SEM) revealed that particles in the matrix of the biofilm coupled extracellular polysaccharides (EPS) and formed sediment in the emitter flow path.Analysis of biofilm mass including protein,polysaccharide and phospholipid fatty acids (PLFAs) showed that emitter flow path style influenced biofilm community structure and diversity.The correlations of biofilm biomass and discharge reduction after 360 h irrigation were computed and suggest that PFLAs provide the best correlation coefficient.Comparatively,the emitter with the unsymmetrical dentate structure and shorter flow path (Emitter C) had the best anti-clogging capability.By optimizing the dentate structure,the internal flow pattern within the flow path could be enhanced as an important method to control the biofilm within emitter flow path.This study established electron microscope techniques and biochemical microbial analysis methods that may provide a framework for future emitter biofilm studies.     

水淬渣人工湿地强化除磷作用研究

研究了水淬渣的磷吸附-解吸效果,构建了以水淬渣为主要基质的模拟垂直流人工湿地系统,分析了水力停留时间(HRT)和污染负荷变化对污水中磷去除的影响,探讨了湿地上行、下行流单元各层基质的除磷贡献.结果表明,水淬渣基质的磷饱和吸附量为3 333 mg.kg-1,其水溶性钙含量为0.084%,pH值为7.54,适合作为湿地除磷基质.HRT与磷除去率呈正相关,当HRT从1 d缩短为0.5 d时,TP去除率降低5.9%~4.7%,当HRT从2 d缩短为1 d时,TP去除率降低2.4%~4.7%,HRT为1 d条件下,水淬渣湿地的磷去除率>85%,说明无限延长HRT无益于强化除磷,适宜的HRT为1 d.在进水浓度稳定的条件下,进水污染负荷与磷去除率呈负相关,当污染负荷范围在12.2~36.8 g.(m2.d)-1时,水淬渣湿地的磷除去率可维持在85%,当污染负荷达到48.9 g.(m2.d)-1后,水淬渣湿地的磷除去率下降至65%,当污染负荷<36.8 g.(m2.d)-1时,水淬渣湿地的磷去除率>82%,说明高污染负荷可抑制基质表面及孔隙中Ca、Al等吸附磷的活跃位点,适宜的进水污染负荷为24.5~36.8g.(m2.d...     

鸡粪腐解过程中不同溶性腐殖质结合铜的变化

以鸡粪为材料,添加不同比例的铜锌进行腐解试验,研究了腐解过程中不同溶性腐殖质结合态铜(水溶性、氢氧化钠溶性、氢氧化钠-焦磷酸钠混合液溶性)浓度的动态变化、受锌含量的影响及其与有效铜的关系.结果表明,粪肥原样H2O-Cu(水溶性腐殖质结合态铜)占其全铜量的10.97%,在腐解过程中先上升后下降;随着粪肥中添加铜量的增加(1:1、2:1、3:1处理),H2O-Cu占其全铜的比例相应减少了(平均分别占其全铜的比例的7.10%、5.18%和3.74%);H2O-Cu随着腐解时间延长呈增加趋势;在腐解的后期(45、60d),粪肥中锌含量的增加会降低H2O-Cu含量.腐解初期粪肥原样NaOH浸提腐殖质-铜(NaOH-Cu)占其全铜量的70.87%,随腐解进行其比例大幅度下降;NaOH-Cu占其全铜的比例随着加入铜的增大而有所下降,分别为55.59%、46.04%和38.08%,且随着腐解时间延长呈下降趋势;粪肥中锌含量的增加对NaOH-Cu含量变化影响较小.粪肥原样中NaOH-Na4P2O7提取腐殖质结合态铜(NaOH-Na4P2O7-Cu)占其全铜量的24.29%,随腐解过程呈增加趋势,NaOH-Na4P2O7-Cu量随着加入铜量的增加而增加,占其全铜比例的15%～25%;粪肥中锌含量增加对NaOH-Na4P2O7-Cu有促进作用.粪肥添加铜锌后,3种浸提剂提取的可溶性腐殖质结合态铜有55%～80%分配在NaOH的溶液中,10%～30%分配在NaOH-Na4P2O7碱性混合液中,0～10%在水溶液中;随加入铜含量和锌含量的增加,NaOH-Na4P2O7-Cu平均分配比(占3种町浸提性腐殖质-Cu的比例)增加,NaOH-Cu和H2O-Cu的分配比减少.相关性分析结果表明:H2O-Cu、NaOH-Cu和NaOH-Na4P2O7-Cu之间显著正相关,它们与有效铜之间呈显著正相关关系(p<0.01).     

水固液微界面氧化还原反应过程与污染物控制研究

本文介绍了3个反应体系,包括铁锰复合氧化物氧化吸附除砷体系、铁氧化物包覆零价铁光芬顿催化和负载型多价态锰氧化物臭氧催化体系,通过固液微界面不同的氧化还原反应,实现了对水中砷和难降解有机污染物的高效去除.重点介绍了不同氧化还原反应对污染物转移转化的作用机制,说明了水体中固液微界面氧化还原反应,对污染物的转移转化起着重要作用.